PAN is one of a class of common air pollutants formed by the action of
sunlight on volatile organic compounds and nitrogen oxides. No toxico
kinetic studies have been found in the available literature. The acute
toxicity of PAN is less than that of ozone, similar to NO2 and higher
than SO2. The LC50 in mice and rats were 718-743 mg/m(3) (for 2 h) an
d 470 mg/m(3) (for 4 h), respectively. Following acute exposure, sever
e lung lesions and, at the higher levels, damage to the epithelium of
upper parts of the respiratory tract were found in animals. It seems t
hat concentrations of 1.19-1.49 mg/m(3) lie not far from the threshold
required for pulmonary function effects in sensitive individuals. How
ever, these PAN concentrations are well above the maximum ambient conc
entrations usually experienced within the USA and Canada (0.003-0.078
mg/m(3)). It appears unlikely that present ambient PAN concentrations
would affect pulmonary lowest level causing eye irritations was 0.64 m
g/m(3) for 2 h. Concentrations of 0.99 and 4.95 mg/m(3) were identifie
d as no-observed-effect level (NOEL) and no-observed-adverse-effect le
vel (NOAEL) for pathological and histological changes in the respirato
ry system (nasal passages) of rats during subchronic exposures to PAN,
but were not considered to be relevant to derivation of a RfC for chr
onic inhalation exposure. PAN is a weak point mutagen or clastogen. Th
e data are not sufficient to evaluate its carcinogenicity. No study wa
s found which could be used for the derivation of a RfC for acute or c
hronic inhalation exposure to PAN.